[go: up one dir, main page]

CN106732621A - Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof - Google Patents

Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof Download PDF

Info

Publication number
CN106732621A
CN106732621A CN201610952445.9A CN201610952445A CN106732621A CN 106732621 A CN106732621 A CN 106732621A CN 201610952445 A CN201610952445 A CN 201610952445A CN 106732621 A CN106732621 A CN 106732621A
Authority
CN
China
Prior art keywords
catalyst
catalytic combustion
sulfur
carrier
copper
Prior art date
Legal status (The legal status is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the status listed.)
Pending
Application number
CN201610952445.9A
Other languages
Chinese (zh)
Inventor
徐炎华
刘志英
张悦
李溪
于鹏
钱红雅
Current Assignee (The listed assignees may be inaccurate. Google has not performed a legal analysis and makes no representation or warranty as to the accuracy of the list.)
Nanjing Tech University
Original Assignee
Nanjing Tech University
Priority date (The priority date is an assumption and is not a legal conclusion. Google has not performed a legal analysis and makes no representation as to the accuracy of the date listed.)
Filing date
Publication date
Application filed by Nanjing Tech University filed Critical Nanjing Tech University
Priority to CN201610952445.9A priority Critical patent/CN106732621A/en
Publication of CN106732621A publication Critical patent/CN106732621A/en
Pending legal-status Critical Current

Links

Classifications

    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J29/00Catalysts comprising molecular sieves
    • B01J29/04Catalysts comprising molecular sieves having base-exchange properties, e.g. crystalline zeolites
    • B01J29/06Crystalline aluminosilicate zeolites; Isomorphous compounds thereof
    • B01J29/70Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65
    • B01J29/72Crystalline aluminosilicate zeolites; Isomorphous compounds thereof of types characterised by their specific structure not provided for in groups B01J29/08 - B01J29/65 containing iron group metals, noble metals or copper
    • B01J29/7207A-type
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/002Mixed oxides other than spinels, e.g. perovskite
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J23/00Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00
    • B01J23/70Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper
    • B01J23/76Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36
    • B01J23/83Catalysts comprising metals or metal oxides or hydroxides, not provided for in group B01J21/00 of the iron group metals or copper combined with metals, oxides or hydroxides provided for in groups B01J23/02 - B01J23/36 with rare earths or actinides
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G7/00Incinerators or other apparatus for consuming industrial waste, e.g. chemicals
    • F23G7/06Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases
    • F23G7/07Incinerators or other apparatus for consuming industrial waste, e.g. chemicals of waste gases or noxious gases, e.g. exhaust gases in which combustion takes place in the presence of catalytic material
    • BPERFORMING OPERATIONS; TRANSPORTING
    • B01PHYSICAL OR CHEMICAL PROCESSES OR APPARATUS IN GENERAL
    • B01JCHEMICAL OR PHYSICAL PROCESSES, e.g. CATALYSIS OR COLLOID CHEMISTRY; THEIR RELEVANT APPARATUS
    • B01J2523/00Constitutive chemical elements of heterogeneous catalysts
    • FMECHANICAL ENGINEERING; LIGHTING; HEATING; WEAPONS; BLASTING
    • F23COMBUSTION APPARATUS; COMBUSTION PROCESSES
    • F23GCREMATION FURNACES; CONSUMING WASTE PRODUCTS BY COMBUSTION
    • F23G2209/00Specific waste
    • F23G2209/14Gaseous waste or fumes

Landscapes

  • Chemical & Material Sciences (AREA)
  • Engineering & Computer Science (AREA)
  • Materials Engineering (AREA)
  • Chemical Kinetics & Catalysis (AREA)
  • Organic Chemistry (AREA)
  • Environmental & Geological Engineering (AREA)
  • Crystallography & Structural Chemistry (AREA)
  • Mechanical Engineering (AREA)
  • General Engineering & Computer Science (AREA)
  • Catalysts (AREA)

Abstract

本发明公开了一种抗硫催化燃烧催化剂及制备方法和应用。所述的催化剂以γ‑Al2O3或5A分子筛为载体,以铜钴固溶体氧化物和铈氧化物,或者是铜钴固溶体氧化物为活性组分;其中活性组分负载质量为载体质量的10%~20%,所述催化剂采用超声‑等体积浸渍方法制备,所制备的催化剂适用于催化燃烧消除工业可挥发性有机废气污染。本发明催化剂在处理有机废气的催化燃烧中具备一定抗硫性,具有高活性、高稳定性,制备方法简单等优点。

The invention discloses a sulfur-resistant catalytic combustion catalyst, a preparation method and an application. The catalyst uses γ-Al 2 O 3 or 5A molecular sieve as a carrier, and copper-cobalt solid solution oxide and cerium oxide, or copper-cobalt solid solution oxide as active components; wherein the active component load mass is the mass of the carrier 10% to 20%, the catalyst is prepared by an ultrasonic-equal volume impregnation method, and the prepared catalyst is suitable for catalytic combustion to eliminate industrial volatile organic waste gas pollution. The catalyst of the invention has certain sulfur resistance in the catalytic combustion of organic waste gas, has the advantages of high activity, high stability, simple preparation method and the like.

Description

一种抗硫催化燃烧催化剂及制备方法和应用A kind of anti-sulfur catalytic combustion catalyst and its preparation method and application

技术领域technical field

本发明属于环境保护催化材料和大气污染治理领域,尤其涉及一种抗硫催化燃烧催化剂及制备方法和应用。The invention belongs to the fields of environmental protection catalytic materials and air pollution control, and in particular relates to a sulfur-resistant catalytic combustion catalyst, a preparation method and an application.

背景技术Background technique

随着化工行业的快速发展,以挥发性有机物(VOCs)为主的废气排放不仅对人类健康造成很大危害,还会促进城市光化学烟雾和霾的生成,严重污染大气环境。因此,对于挥发性有机物的治理引起各级环保部门和企业的关注。With the rapid development of the chemical industry, volatile organic compounds (VOCs)-based exhaust emissions not only cause great harm to human health, but also promote the generation of urban photochemical smog and haze, seriously polluting the atmospheric environment. Therefore, the control of volatile organic compounds has attracted the attention of environmental protection departments and enterprises at all levels.

常用的VOCs处理技术包括热力燃烧、催化燃烧、吸附、生物处理、等离子体氧化和光催化氧化等。其中,催化燃烧法指有催化剂存在的条件下,使有机废气在在低温下发生无焰燃烧,生成二氧化碳和水等无害物质,达到治理的目的。催化燃烧技术具有能耗低、燃烧效率高、起燃温度低和二次污染小等特点,是应用广泛的VOCs处理技术。催化燃烧技术的关键在于选择和研制合适的催化剂。Commonly used VOCs treatment technologies include thermal combustion, catalytic combustion, adsorption, biological treatment, plasma oxidation, and photocatalytic oxidation. Among them, the catalytic combustion method refers to the flameless combustion of organic waste gas at low temperature in the presence of a catalyst to generate harmless substances such as carbon dioxide and water to achieve the purpose of treatment. Catalytic combustion technology has the characteristics of low energy consumption, high combustion efficiency, low ignition temperature and low secondary pollution, and is a widely used VOCs treatment technology. The key to catalytic combustion technology is to select and develop a suitable catalyst.

专利CN102441404A公开了一种抗硫催化燃烧催化剂及其制备方法,解决了现有技术中催化剂易发生硫中毒的问题。该催化剂采用贵金属Pt为活性组分,以蜂窝陶瓷为载体,其中贵金属担载量为每升催化剂0.2~3.5g,按涂层的总重量计,活性Al2O340%~85%,TiO25%~50%,CeO25%~15%,La2O32%~10%,CuO、MnO2、NiO、Fe2O3中的一种或几种3%~15%。但贵金属催化剂存在来源少、价格昂贵、易中毒等缺点,阻碍了其应用。Patent CN102441404A discloses a sulfur-resistant catalytic combustion catalyst and its preparation method, which solves the problem that the catalyst is prone to sulfur poisoning in the prior art. The catalyst uses noble metal Pt as the active component and honeycomb ceramics as the carrier, wherein the noble metal load is 0.2-3.5g per liter of catalyst, and the active Al 2 O 3 is 40%-85% based on the total weight of the coating, TiO 2 5%-50%, CeO 2 5%-15%, La 2 O 3 2%-10%, one or more of CuO, MnO 2 , NiO, Fe 2 O 3 3%-15%. However, noble metal catalysts have disadvantages such as few sources, high price, and easy poisoning, which hinder their application.

基于以上分析,开发一种成本低、活性高、抗硫性和稳定性好的催化剂具有重要的实用价值。Based on the above analysis, it is of great practical value to develop a catalyst with low cost, high activity, good sulfur resistance and stability.

发明内容Contents of the invention

本发明的目的是针对现有贵金属催化剂成本高、易发生硫中毒的缺点,提供一种价格低廉、催化活性优良、具备一定抗硫性的抗硫催化燃烧催化剂,本发明的另一目的是提供上述催化剂的制备方法,本发明还有和目的是提供上述催化剂的应用。The object of the present invention is to provide a sulfur-resistant catalytic combustion catalyst with low price, excellent catalytic activity and certain sulfur resistance in view of the shortcomings of the existing noble metal catalysts, which are high in cost and prone to sulfur poisoning. Another object of the present invention is to provide The preparation method of the above-mentioned catalyst, the present invention also aims to provide the application of the above-mentioned catalyst.

本发明的技术方案如下:一种抗硫催化燃烧催化剂,其特征在于:以γ-Al2O3或5A分子筛为载体,以铜钴固溶体氧化物和铈氧化物,或者是铜钴固溶体氧化物为活性组分;其中活性组分负载质量为载体质量的10%~20%。The technical scheme of the present invention is as follows: a sulfur-resistant catalytic combustion catalyst, characterized in that: γ-Al 2 O 3 or 5A molecular sieve is used as a carrier, copper-cobalt solid solution oxide and cerium oxide, or copper-cobalt solid solution oxide It is an active component; wherein the load mass of the active component is 10% to 20% of the mass of the carrier.

优选上述的载体目数为16~40目。优选上述的催化剂活性组分中铜、钴和铈的摩尔比为1:(1.8-2.1):(0~1.5)。Preferably, the mesh number of the above-mentioned carrier is 16-40 mesh. Preferably, the molar ratio of copper, cobalt and cerium in the above catalyst active components is 1:(1.8-2.1):(0-1.5).

本发明还提供了上述的抗硫催化燃烧的制备方法,其具体步骤如下:配制硝酸铜、硝酸钴和硝酸铈溶液,将三种硝酸盐溶液按照铜、钴和铈的摩尔比为1:(1.8~2.1):(0~1.5)混合;将载体在烘箱中干燥后;在向所配制的混合液中加入干燥后的载体,在超声装置中超声搅拌,充分混合均匀;将所得混合物在烘箱中干燥;将干燥后的混合物置于马弗炉中500~800℃焙烧4~5小时,即得抗硫催化燃烧催化剂。The present invention also provides the preparation method of above-mentioned anti-sulfur catalytic combustion, and its concrete steps are as follows: preparation copper nitrate, cobalt nitrate and cerium nitrate solution, three kinds of nitrate solutions are 1 according to the molar ratio of copper, cobalt and cerium:( 1.8~2.1): (0~1.5) mixed; after the carrier is dried in the oven; add the dried carrier to the prepared mixed solution, ultrasonically stir in the ultrasonic device, and mix well; the resulting mixture is placed in the oven drying in medium temperature; put the dried mixture in a muffle furnace and bake at 500-800°C for 4-5 hours to obtain the anti-sulfur catalytic combustion catalyst.

优选上述载体在烘箱中干燥的温度为100-120℃,干燥时间为4~6小时;混合物在烘箱中干燥的温度为100-120℃,干燥时间为10-14小时。Preferably, the drying temperature of the above-mentioned carrier in the oven is 100-120° C., and the drying time is 4-6 hours; the drying temperature of the mixture in the oven is 100-120° C., and the drying time is 10-14 hours.

优选上述超声装置中的超声频率20kHz-28kHz,搅拌时间为0.5~2小时。Preferably, the ultrasonic frequency in the ultrasonic device is 20kHz-28kHz, and the stirring time is 0.5-2 hours.

本发明还提供了上述的抗硫催化燃烧催化剂在挥发性有机废气的催化燃烧处理中的应用。The present invention also provides the application of the above-mentioned anti-sulfur catalytic combustion catalyst in the catalytic combustion treatment of volatile organic waste gas.

优选上述的挥发性有机废气为苯、甲苯或二甲苯。Preferably, the above-mentioned volatile organic waste gas is benzene, toluene or xylene.

催化燃烧反应在固定床反应器中进行:将10ml催化剂置于反应管等温区,催化剂床层上下分别填加小颗粒的石英砂,以减少死体积。反应器为内径12mm,长1000mm不锈钢管,电热套加热保温,进气通过催化剂床层前由质量流量计控制空气流量为1L/min,原料气通过0℃冰水浴以控制有机物蒸汽压,控制进气浓度为4113mg/m3,所述的催化燃烧反应温度为180℃~420℃,反应尾气通过气相色谱仪进行分析。The catalytic combustion reaction is carried out in a fixed-bed reactor: 10ml of catalyst is placed in the isothermal zone of the reaction tube, and small particles of quartz sand are added above and below the catalyst bed to reduce dead volume. The reactor is a stainless steel tube with an inner diameter of 12 mm and a length of 1000 mm. The electric heating mantle is used for heating and heat preservation. The gas concentration is 4113mg/m 3 , the catalytic combustion reaction temperature is 180°C-420°C, and the reaction tail gas is analyzed by gas chromatography.

有益效果:Beneficial effect:

本发明催化剂适用于VOCs催化燃烧,具有以下优点:The catalyst of the present invention is suitable for catalytic combustion of VOCs and has the following advantages:

1、本发明研究开发的催化剂应用于挥发性有机废气催化燃烧中,区别于传统应用于贵金属催化燃烧催化剂,以非贵金属氧化物为主要活性组分,原料易得。1. The catalyst researched and developed by the present invention is used in the catalytic combustion of volatile organic waste gas, which is different from the traditional application of noble metal catalytic combustion catalysts, with non-noble metal oxides as the main active components, and the raw materials are easy to obtain.

2、通过负载特定的金属元素,在特定条件、配比并优化制备过程,使得催化剂表面能够形成固溶体和稀土金属氧化物,具备一定的抗硫中毒性,对苯系物如甲苯具有较高催化活性。2. By loading specific metal elements, under specific conditions, proportioning and optimizing the preparation process, the surface of the catalyst can form solid solutions and rare earth metal oxides, which has a certain resistance to sulfur poisoning and has a high catalytic effect on benzene series such as toluene active.

3、稀土元素的加入还能够提高催化剂分散度,在高温条件下也不容易烧结,克服传统贵金属催化剂高温易烧结的问题。3. The addition of rare earth elements can also improve the dispersion of the catalyst, and it is not easy to sinter under high temperature conditions, which overcomes the problem that traditional precious metal catalysts are easy to sinter at high temperatures.

附图说明Description of drawings

图1实施例2制得的10%Cu-Co-O/5A分子筛催化剂表面SEM图;The 10%Cu-Co-O/5A molecular sieve catalyst surface SEM picture that Fig. 1 embodiment 2 makes;

图2实施例3制得的20%CeO2/Cu-Co-O/γ-Al2O3催化剂表面SEM图。Fig. 2 is the SEM image of the surface of the 20% CeO 2 /Cu-Co-O/γ-Al 2 O 3 catalyst prepared in Example 3.

具体实施方式detailed description

下面结合实施例来对本发明进一步详细说明,其中部分制备条件仅是作为典型情况的说明,并非是对本发明的限定。The present invention will be further described in detail below in conjunction with the examples, wherein some preparation conditions are only used as illustrations of typical cases, and are not intended to limit the present invention.

实施例1Example 1

将破碎过筛后的γ-Al2O3载体(16~30目)于烘箱中110℃下干燥4小时。称取4.03gCu(NO3)2·3H2O、9.70gCo(NO3)2·6H2O,其中铜钴原子比为1:2,加入一定量去离子水溶解配置成25ml溶液。将20gγ-Al2O3载体等体积浸渍于上述混合溶液,在超声频率25kHz下超声震荡40min,110℃下干燥13h,马弗炉600℃焙烧5h,即可制得负载量为20%Cu-Co-O/γ-Al2O3催化剂。The crushed and sieved γ-Al 2 O 3 carrier (16-30 mesh) was dried in an oven at 110° C. for 4 hours. Weigh 4.03g Cu(NO 3 ) 2 ·3H 2 O and 9.70g Co(NO 3 ) 2 ·6H 2 O, wherein the atomic ratio of copper to cobalt is 1:2, add a certain amount of deionized water to dissolve and prepare a 25ml solution. Immerse 20g of γ-Al 2 O 3 support in equal volume in the above mixed solution, ultrasonically vibrate for 40min at an ultrasonic frequency of 25kHz, dry at 110°C for 13h, and bake at 600°C in a muffle furnace for 5h to obtain a 20% Cu- Co-O/γ-Al 2 O 3 catalyst.

实施例2Example 2

将破碎过筛后的5A分子筛载体(20~40目)于烘箱中120℃干燥4小时。称取2.01gCu(NO3)2·3H2O、4.35gCo(NO3)2·6H2O,其中铜钴原子比为1:2,加入一定量去离子水溶解配置成28ml溶液。将20g5A分子筛载体等体积浸渍于上述混合溶液,在超声频率20kHz下超声震荡100min,110℃下干燥12h,马弗炉500℃焙烧5h,即可制得负载量为10%Cu-Co-O/5A分子筛催化剂。催化剂表面SEM图见附图1。由图1可以看出,催化剂表面的氧化铜、氧化钴晶体颗粒较小,分布均匀,且负载之后催化剂仍具备分子筛原有的孔道结构。The crushed and sieved 5A molecular sieve carrier (20-40 mesh) was dried in an oven at 120° C. for 4 hours. Weigh 2.01g Cu(NO 3 ) 2 ·3H 2 O and 4.35g Co(NO 3 ) 2 ·6H 2 O, wherein the copper-cobalt atomic ratio is 1:2, add a certain amount of deionized water to dissolve and prepare a 28ml solution. Immerse 20g of 5A molecular sieve carrier in equal volume in the above mixed solution, ultrasonically vibrate at an ultrasonic frequency of 20kHz for 100min, dry at 110°C for 12h, and bake at 500°C in a muffle furnace for 5h to obtain a 10% Cu-Co-O/ 5A molecular sieve catalyst. The SEM image of the catalyst surface is shown in Figure 1. It can be seen from Figure 1 that the copper oxide and cobalt oxide crystal particles on the surface of the catalyst are small and evenly distributed, and the catalyst still has the original pore structure of the molecular sieve after loading.

实施例3Example 3

将破碎过筛后的γ-Al2O3载体(16~30目)于烘箱中110℃下干燥6小时。称取4.03gCu(NO3)2·3H2O、9.70gCo(NO3)2·6H2O、7.74gCe(NO3)2·6H2O,其中铜钴铈原子比为1:2:1,加入一定量去离子水溶解,混合得到活性组分溶液。将20gγ-Al2O3载体等体积浸渍于上述混合溶液中,在超声频率28kHz下超声震荡35min,120℃下干燥10h,马弗炉600℃焙烧5h,即可制得负载量20%CeO2/Cu-Co-O/γ-Al2O3催化剂。催化剂表面SEM图见附图2。由图2可以看出,负载之后催化剂仍具备三氧化二铝多孔结构。The crushed and sieved γ-Al 2 O 3 carrier (16-30 mesh) was dried in an oven at 110° C. for 6 hours. Weigh 4.03gCu(NO 3 )2·3H 2 O, 9.70gCo(NO 3 ) 2 ·6H 2 O, 7.74gCe(NO 3 ) 2 ·6H 2 O, wherein the atomic ratio of copper, cobalt and cerium is 1:2:1 , add a certain amount of deionized water to dissolve, and mix to obtain the active component solution. Immerse 20g of γ-Al2O3 support in equal volume in the above mixed solution, ultrasonically vibrate at an ultrasonic frequency of 28kHz for 35min, dry at 120°C for 10h, and bake in a muffle furnace at 600°C for 5h to obtain a 20% CeO 2 /Cu- Co-O/γ-Al 2 O 3 catalyst. The SEM image of the catalyst surface is shown in Figure 2. It can be seen from Figure 2 that the catalyst still has a porous structure of alumina after loading.

对比例1Comparative example 1

将破碎过筛后的γ-Al2O3载体(16~30目)于烘箱中110℃下干燥4~6小时。称取10.85gCo(NO3)2·6H2O,加入一定量去离子水溶解,混合得到活性组分溶液。将20gγ-Al2O3载体等体积浸渍于上述混合溶液中,超声震荡40min,110℃下干燥6h,马弗炉500℃焙烧4h,即可制得负载量20%CoOx/γ-Al2O3催化剂。The crushed and sieved γ-Al 2 O 3 carrier (16-30 mesh) was dried in an oven at 110° C. for 4-6 hours. Weigh 10.85g Co(NO 3 ) 2 ·6H2O, add a certain amount of deionized water to dissolve, and mix to obtain an active component solution. Immerse 20g of γ-Al 2 O 3 support in equal volume in the above mixed solution, oscillate ultrasonically for 40min, dry at 110°C for 6h, and bake in muffle furnace at 500°C for 4h to obtain a loading capacity of 20% CoO x /γ- Al2 O3 catalyst.

实施例4Example 4

按照实施例3制备好的复合氧化物催化剂的催化燃烧活性测试在固定床反应器中进行:将10ml催化剂置于反应管等温区,催化剂床层上下分别填加小颗粒的石英砂,以减少死体积。反应器为内径12mm,长1000mm不锈钢管,电热套加热保温,进气通过催化剂床层前由质量流量计控制空气流量为1L/min,原料气通过0℃冰水浴以控制有机物蒸汽压,控制进气浓度为4113mg/m3,所述的催化燃烧反应温度为180℃~420℃,反应尾气通过气相色谱仪进行分析,记录不同有机气体不同转化率时的反应温度,结果见表1。由表1可知,本发明制备的催化剂具有较高催化活性。The catalytic combustion activity test of the composite oxide catalyst prepared according to Example 3 is carried out in a fixed-bed reactor: 10ml of catalyst is placed in the isothermal zone of the reaction tube, and the upper and lower sides of the catalyst bed are respectively filled with small particles of quartz sand to reduce dead volume. The reactor is a stainless steel tube with an inner diameter of 12 mm and a length of 1000 mm. The electric heating mantle is used for heating and heat preservation. The gas concentration was 4113 mg/m 3 , and the catalytic combustion reaction temperature was 180°C-420°C. The reaction tail gas was analyzed by gas chromatography, and the reaction temperatures at different conversion rates of different organic gases were recorded. The results are shown in Table 1. As can be seen from Table 1, the catalyst prepared by the present invention has higher catalytic activity.

实施例5Example 5

将上述实施例1-3方法制备的催化剂,以及对比例1方法制备的催化剂,由实施例4所述的装置下进行甲苯催化燃烧评价,结果如表2。The catalyst prepared by the method of the above-mentioned Examples 1-3 and the catalyst prepared by the method of Comparative Example 1 were evaluated by the device described in Example 4 for catalytic combustion of toluene, and the results are shown in Table 2.

实施例6Example 6

将实例3中催化剂用500ppm、流速为1ml/s的SO2处理30min后,于实施例4所述装置下进行甲苯催化活性评价,结果如表2。Catalyst among the example 3 is used 500ppm, flow velocity is the SO of 1ml/s After 30min, carry out toluene catalytic activity evaluation under the apparatus described in embodiment 4, the result is as table 2.

表1催化燃烧各类VOCs的活性Table 1 Catalytic combustion activity of various VOCs

表2催化剂活性评价结果Table 2 Catalyst activity evaluation results

通过以上实验对比可见,本发明用于挥发性有机物催化燃烧净化处理时,催化剂具有较高催化活性,具有很高的热稳定性。本发明制备的催化剂实用性强、制备方法采用等体积浸渍法,工艺简单且绿色环保,催化剂生产成本较低,故有望取代目前工业贵金属催化剂。It can be seen from the comparison of the above experiments that when the present invention is used for catalytic combustion and purification treatment of volatile organic compounds, the catalyst has relatively high catalytic activity and high thermal stability. The catalyst prepared by the invention has strong practicability, the preparation method adopts an equal-volume impregnation method, the process is simple and environmentally friendly, and the catalyst production cost is low, so it is expected to replace the current industrial precious metal catalyst.

Claims (8)

1. a kind of Sulfur-resistant catalytic combustion catalyst, it is characterised in that:With γ-Al2O3Or 5A molecular sieves are carrier, with copper cobalt solid solution Oxide body and cerium oxide, or copper cobalt solid solution, oxide are active component;Wherein active component load quality is load The 10%~20% of weight.
2. Sulfur-resistant catalytic combustion catalyst according to claim 1, it is characterised in that described carrier mesh number is 16~40 Mesh.
3. Sulfur-resistant catalytic combustion catalyst according to claim 1, it is characterised in that in described catalyst activity component The mol ratio of copper, cobalt and cerium is 1:(1.8-2.1):(0~1.5).
4. a kind of to prepare the method that sulfur resistive catalysis as claimed in claim 1 is burnt, it is comprised the following steps that:Preparation copper nitrate, Cobalt nitrate, cerous nitrate solution, by three kinds of nitrate solutions according to copper cobalt cerium mol ratio be 1:(1.8~2.1):(0~1.5) mix Close;After carrier is dried in an oven;Dried carrier is added in the mixed liquor prepared, the ultrasound in Vltrasonic device Stirring, is sufficiently mixed uniform;Gained mixture is dried in an oven;Dried mixture is placed in 500 in Muffle furnace~ 800 DEG C are calcined 4~5 hours, obtain final product Sulfur-resistant catalytic combustion catalyst.
5. method according to claim 4, it is characterised in that dry temperature is carrier in an oven
100-120 DEG C, drying time is 4~6 hours;Dry temperature is 100-120 DEG C, drying time to mixture in an oven It is 10-14 hours.
6. method according to claim 4, it is characterised in that the supersonic frequency 20kHz-28kHz in Vltrasonic device, stirring Time is 0.5~2 hour.
7. a kind of Sulfur-resistant catalytic combustion catalyst as claimed in claim 1 is in the catalysis burning treatment of volatile organic waste gas Application.
8. application according to claim 7, it is characterised in that described volatile organic waste gas are benzene, toluene or diformazan Benzene.
CN201610952445.9A 2016-10-27 2016-10-27 Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof Pending CN106732621A (en)

Priority Applications (1)

Application Number Priority Date Filing Date Title
CN201610952445.9A CN106732621A (en) 2016-10-27 2016-10-27 Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof

Applications Claiming Priority (1)

Application Number Priority Date Filing Date Title
CN201610952445.9A CN106732621A (en) 2016-10-27 2016-10-27 Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof

Publications (1)

Publication Number Publication Date
CN106732621A true CN106732621A (en) 2017-05-31

Family

ID=58972722

Family Applications (1)

Application Number Title Priority Date Filing Date
CN201610952445.9A Pending CN106732621A (en) 2016-10-27 2016-10-27 Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof

Country Status (1)

Country Link
CN (1) CN106732621A (en)

Cited By (6)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107376929A (en) * 2017-08-09 2017-11-24 南京工业大学 Catalytic combustion catalyst, preparation and application thereof
CN109304154A (en) * 2017-11-16 2019-02-05 中国石油化工股份有限公司 A kind of order mesoporous TMCO- aluminium oxide catalyst and preparation method thereof that sulfur resistive is poisoned
CN113333015A (en) * 2021-04-21 2021-09-03 浙江理工大学 Chlorine-containing organic waste gas catalytic combustion catalyst with high carbon dioxide selectivity, and preparation and application thereof
CN114558589A (en) * 2022-03-22 2022-05-31 深圳市朗石科学仪器有限公司 Total Organic Carbon (TOC) catalyst and preparation method and application thereof
CN114713221A (en) * 2022-04-25 2022-07-08 南京工业大学 Preparation method of efficient sulfur poisoning resistant catalyst for VOCs treatment
CN114768814A (en) * 2022-04-24 2022-07-22 湖南匡楚科技有限公司 Preparation method of catalyst for catalytic combustion of VOCs and product thereof

Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101322942A (en) * 2008-07-29 2008-12-17 西南化工研究设计院 Oxygen-containing coal bed gas deoxidation catalyst and preparation thereof as well as applications
CN101716511A (en) * 2009-11-27 2010-06-02 南京工业大学 Catalyst for catalytic combustion of industrial organic waste gas and preparation method thereof
CN104053503A (en) * 2012-01-19 2014-09-17 丰田自动车株式会社 Exhaust gas purification catalyst and manufacturing method thereof
CN105879901A (en) * 2016-05-06 2016-08-24 碗海鹰 Preparation method for supported catalyst for catalyzing combustion of VOCs (Volatile Organic Compounds)

Patent Citations (4)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN101322942A (en) * 2008-07-29 2008-12-17 西南化工研究设计院 Oxygen-containing coal bed gas deoxidation catalyst and preparation thereof as well as applications
CN101716511A (en) * 2009-11-27 2010-06-02 南京工业大学 Catalyst for catalytic combustion of industrial organic waste gas and preparation method thereof
CN104053503A (en) * 2012-01-19 2014-09-17 丰田自动车株式会社 Exhaust gas purification catalyst and manufacturing method thereof
CN105879901A (en) * 2016-05-06 2016-08-24 碗海鹰 Preparation method for supported catalyst for catalyzing combustion of VOCs (Volatile Organic Compounds)

Non-Patent Citations (1)

* Cited by examiner, † Cited by third party
Title
张志远 等: "新型Cu-Co-Ox催化剂的制备及其催化燃烧甲苯的性能研究", 《环境污染与防治》 *

Cited By (9)

* Cited by examiner, † Cited by third party
Publication number Priority date Publication date Assignee Title
CN107376929A (en) * 2017-08-09 2017-11-24 南京工业大学 Catalytic combustion catalyst, preparation and application thereof
CN109304154A (en) * 2017-11-16 2019-02-05 中国石油化工股份有限公司 A kind of order mesoporous TMCO- aluminium oxide catalyst and preparation method thereof that sulfur resistive is poisoned
CN109304154B (en) * 2017-11-16 2021-11-05 中国石油化工股份有限公司 Sulfur-poison-resistant ordered mesoporous TMCO-alumina catalyst and preparation method thereof
CN113333015A (en) * 2021-04-21 2021-09-03 浙江理工大学 Chlorine-containing organic waste gas catalytic combustion catalyst with high carbon dioxide selectivity, and preparation and application thereof
CN114558589A (en) * 2022-03-22 2022-05-31 深圳市朗石科学仪器有限公司 Total Organic Carbon (TOC) catalyst and preparation method and application thereof
CN114558589B (en) * 2022-03-22 2024-04-26 深圳市朗石科学仪器有限公司 Total Organic Carbon (TOC) catalyst and preparation method and application thereof
CN114768814A (en) * 2022-04-24 2022-07-22 湖南匡楚科技有限公司 Preparation method of catalyst for catalytic combustion of VOCs and product thereof
CN114713221A (en) * 2022-04-25 2022-07-08 南京工业大学 Preparation method of efficient sulfur poisoning resistant catalyst for VOCs treatment
CN114713221B (en) * 2022-04-25 2023-12-08 南京工业大学 Preparation method of efficient sulfur poisoning resistant catalyst for VOCs treatment

Similar Documents

Publication Publication Date Title
CN106732621A (en) Sulfur-resistant catalytic combustion catalyst, and preparation method and application thereof
CN104646022B (en) A kind of honeycomb fashion low-temperature denitration catalyst and preparation method thereof
Brummer et al. Contribution to cleaner production from the point of view of VOC emissions abatement: A review
CN102240557A (en) A nickel-iron-manganese composite oxide catalyst for treating industrial waste gas and its preparation method
CN112892547B (en) Catalyst for simultaneously removing nitrogen oxide and carbon monoxide and preparation method thereof
CN111229208B (en) Lotus leaf-source biochar-loaded metal oxide low-temperature SCR (selective catalytic reduction) flue gas denitration catalyst and preparation method and application thereof
CN104492255A (en) Method for treating waste gas through adsorption-ozone-catalysis together with adsorption material in-situ regeneration
CN105833901B (en) A kind of PrOx-MnOx/ SAPO-34 low-temperature SCR catalyst for denitrating flue gas and the preparation method and application thereof
CN108816236A (en) A kind of fly ash base VOCs catalyst for catalytic combustion and preparation method thereof
CN103157480B (en) Vanadium oxide/iron oxide denitration catalyst, preparation method and application thereof
CN108686650A (en) A kind of cryptomelane type manganese dioxide, preparation method and use
CN112642496B (en) Regenerated catalyst capable of realizing synchronous denitration and VOCs (volatile organic compounds) and CO and preparation method thereof
CN102513123A (en) Rare earth perovskite type catalyst for treating industrial waste gas and preparation method and application thereof
CN102407130A (en) Preparation method of catalytic combustion composite metal oxide monolithic catalyst
CN109794248A (en) A kind of low-cost flue gas denitration catalyst and preparation and use method thereof
CN108479762A (en) A kind of manganese oxide catalyst and its preparation method and application
CN107511160B (en) MOX/g-C3N4@SiO2Preparation method and application of catalyst
CN109603807B (en) Modified activated carbon Ce-Nb/TiO2@ AC low-temperature efficient desulfurization and denitrification catalyst and preparation method thereof
CN105195170A (en) SCR (Selective Catalytic Reduction) denitration catalyst, and preparation method and application thereof
CN112403487A (en) Medium-low temperature vanadium-free desulfurization and denitrification catalyst and preparation method thereof
CN105642333A (en) Multifunctional environment purification composite material, and preparation method and application thereof
CN112007688A (en) Ruthenium catalyst for low-temperature catalytic oxidation of volatile organic pollutants, and preparation method and application thereof
CN106824217A (en) A kind of cellular integrated catalyst and preparation method thereof
CN101797505B (en) Desulfuration and denitration catalyst and preparation method thereof
CN112691542B (en) Metal composite molecular sieve material for adsorbing-catalytically oxidizing VOCs (volatile organic compounds), and preparation method and application thereof

Legal Events

Date Code Title Description
PB01 Publication
PB01 Publication
SE01 Entry into force of request for substantive examination
SE01 Entry into force of request for substantive examination
RJ01 Rejection of invention patent application after publication
RJ01 Rejection of invention patent application after publication

Application publication date: 20170531